Assessment of Water Quality, Eutrophication, and Zooplankton Community in Lake Burullus, Egypt

Total Page:16

File Type:pdf, Size:1020Kb

Assessment of Water Quality, Eutrophication, and Zooplankton Community in Lake Burullus, Egypt diversity Article Assessment of Water Quality, Eutrophication, and Zooplankton Community in Lake Burullus, Egypt Ahmed E. Alprol 1, Ahmed M. M. Heneash 1, Asgad M. Soliman 1, Mohamed Ashour 1,* , Walaa F. Alsanie 2, Ahmed Gaber 3 and Abdallah Tageldein Mansour 4,5 1 National Institute of Oceanography and Fisheries, NIOF, Cairo 11516, Egypt; [email protected] (A.E.A.); [email protected] (A.M.M.H.); [email protected] (A.M.S.) 2 Department of Clinical Laboratories Sciences, The Faculty of Applied Medical Sciences, Taif University, P.O. Box 11099, Taif 21944, Saudi Arabia; [email protected] 3 Department of Biology, College of Science, Taif University, P.O. Box 11099, Taif 21944, Saudi Arabia; [email protected] 4 Animal and Fish Production Department, College of Agricultural and Food Sciences, King Faisal University, P.O. Box 420, Al-Ahsa 31982, Saudi Arabia; [email protected] 5 Fish and Animal Production Department, Faculty of Agriculture (Saba Basha), Alexandria University, Alexandria 21531, Egypt * Correspondence: [email protected] Abstract: Burullus Lake is Egypt’s second most important coastal lagoon. The present study aimed to shed light on the different types of polluted waters entering the lake from various drains, as well as to evaluate the zooplankton community, determine the physical and chemical characteristics of the waters, and study the eutrophication state based on three years of seasonal monitoring from Citation: Alprol, A.E.; Heneash, 2017 to 2019 at 12 stations. The results revealed that Rotifera, Copepoda, Protozoa, and Cladocera A.M.M. ; Soliman, A.M.; Ashour, M.; dominated the zooplankton population across the three-year study period, with a total of 98 taxa from Alsanie, W.F.; Gaber, A.; Mansour, 59 genera and 10 groups detected in the whole-body lake in 2018 and 2019, compared to 93 species A.T. Assessment of Water Quality, from 52 genera in 2017. Twelve representative surface water samples were collected from the lake to Eutrophication, and Zooplankton determine physicochemical parameters, i.e., temperature, pH, salinity, dissolved oxygen, biological Community in Lake Burullus, Egypt. oxygen demand, chemical oxygen demand, ammonia-N, nitrate–N, nitrate-N, total nitrogen, total Diversity 2021, 13, 268. https:// phosphorus, dissolved reactive phosphorus, and chlorophyll-a, as well as Fe, Cu, Zn, Cr, Ni, Cd, doi.org/10.3390/d13060268 and Pb ions. Based on the calculations of the water quality index (WQI), the lake was classified as having good water quality. However, the trophic state is ranked as hyper-eutrophic and high trophic Academic Editors: Boris A. Levin and conditions. Yulia V. Bespalaya Keywords: zooplankton community; marine pollution; water quality; eutrophication state; heavy Received: 29 April 2021 Accepted: 11 June 2021 metals; Burullus Lake Published: 15 June 2021 Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in 1. Introduction published maps and institutional affil- The Deltaic Mediterranean coastline of Egypt, especially the middle part, has economic iations. importance. From the west coast to the east coast, there are three Deltaic shallow lakes (Edku, Burullus, and Manzala Lakes). Burullus Lake is the second-largest natural lake in Egypt and is situated close to the Mediterranean Sea among the two main branches of the Nile. The importance of lakes as natural resources includes fish production, as they account Copyright: © 2021 by the authors. for more than 40% of the overall fish production in Egypt. As a result of anthropogenic Licensee MDPI, Basel, Switzerland. activity and pollution, its production has decreased to less than 12.22% now [1]. Burullus This article is an open access article Lake is one of a network of protected areas throughout Egypt, designated and managed distributed under the terms and by the Egyptian Environmental Affairs Agency. It is registered as a Ramsar site in 1998. conditions of the Creative Commons Additionally, Birdlife International has identified it as an important bird area (IBA) [2], due Attribution (CC BY) license (https:// to its importance for refuge, migratory foraging, and breeding of water birds [3]. It covers creativecommons.org/licenses/by/ an area of 410 km2 [4] of which 220 km2 are open water [5]. It is observable that the open 4.0/). Diversity 2021, 13, 268. https://doi.org/10.3390/d13060268 https://www.mdpi.com/journal/diversity Diversity 2021, 13, 268 2 of 23 water surface in the lake had reduced from 1092 km2 in 1801 [6] to 434.6 km2 in 1972 then reduced to 220 km2 in 2015 with a reduction of about 80.0% of the water area [5]. Coastal lakes are heavily influenced by anthropogenic activities from watersheds, as they receive inputs of freshwater and polluted waters containing organic and inorganic compounds from different sources [7]. These lakes collect massive amounts of drainage water from various drains around the Nile delta and connect to the Mediterranean Sea via El-Boughaz outlets [2]. Contamination of the marine environment is a major factor that poses a substantial threat to marine creatures’ survival [8]. Among the several pollutants, heavy metals are toxic, persistent, and abundant owing to their accumulation in the food chain and continued persistence in the ecosystem and their concentration increases through biomagnification [9]. The impacts of pollution have far-reaching consequences for public health, the economy, and the environment [10]. The process of eutrophication is driven by an increase in nutrients in the aquatic systems, particularly nitrogen and phosphorus in the ecosystem, which leads to an increase in primary production (photosynthesis) and an accumulation of organic matter in the lakes. In addition, silt from the drainage basins will accumulate over time, which makes the lake shallower and warmer. Eutrophication can also have a negative impact on the reservoir ecology as well as the natural stability of the lake, affecting practically all of the biological communities and their interactions in the water body [11]. Under natural conditions, the rate of this process is very slow and it takes hundreds or thousands of years. Zooplankton are aquatic species with poor swimming abilities that float in the water column of ocean, seas, or freshwater bodies to travel for long distances [8,12,13]. Zooplank- tons are important in the ecosystem because they connect the primary production and the higher levels, monitoring water quality, pollution, and the state of eutrophication [14,15]. In addition, zooplankton play an important role in the natural cycle of carbon and other elements in the sea [16]. On the other hand, zooplankton are the main suitable feeds for larval stages of many fish and shellfish species in marine hatcheries [8,12]. Seasonal zooplankton movement and the factors driving their inconstancy are very sensitive to changes in ecological variables, particularly in shallow, semi-enclosed inlets with densely populated shores, where increasing anthropogenic nutrient input has a serious influence on marine communities [17,18]. Monitoring of water quality is the first step that can lead to management and conservation of aquatic ecosystems. The chemical and physical factors influencing the marine environment include temperature, pH, salinity, dissolved oxygen, biological oxygen demand, chemical oxygen demand, nutrients, reactive phosphate, heavy metal pollutants, and others. These parameters are considered the most limiting factors affecting the survival and growth of aquatic organisms [19–21]. Poor water quality could be produced via low aquatic flow, municipal discharges, and wastewater effluents [22]. In this study, Burullus Lake was chosen because of its economic importance in Egypt, based on its various uses and surroundings, such as tourism, fisheries activity, nutrient enrichment, and industrial water sources, among others. Furthermore, any noticeable change in water quality has an impact on the health, structure, and growth of the fish population, so this paper aims to determine most of the parameters related to water quality and identify the major sources of pollution in Burullus Lake, Egypt over the course of three years, from 2017–2019, in conjunction with the study of eutrophication state and an assessment of potential ecological concerns. In addition, it aims to assess the community, occurrence, diversity, and abundance of zooplankton in Burullus Lake. Moreover, the current study will be a useful tool in assisting decision makers and authorities in charge for sustainable marine management and increasing the lake production. 2. Materials and Methods 2.1. Study Area and Sampling Burullus Lake is located at (30◦220–31◦350 N; 30◦330–31◦080 E) with an area of about 460 km2, length of about 47 km, and width ranges between 6 and 16 km. It has an irregular elongated shape with 0.4–2.5 m depth. The lake receives seawater through a long canal Diversity 2021, 13, 268 3 of 23 (Boughaz El-Burullus) that connects the lake to the sea. Fresh water enters the lake through 8 drains and 1 freshwater canal. The lake is divided into 3 basins; eastern, middle, and western. It is situated on the eastern port of Rosetta side of the River Nile. Water samples were collected seasonally for the period from winter 2017 to autumn 2019 in sterile containers and maintained in an icebox on the site. A total of 12 surface water samples were collected from 12 sites representing different environmental habitats. Information of the sampling sites with their latitude and longitude are presented in Table1 and Figure1. 2.2. Methods Analyses of the physicochemical parameters of collected water samples were in- vestigated according to the standard methods APHA [23] to estimate various factors, such as biological oxygen demand (BOD), chemical oxygen demand (COD), ammonia-N, nitrate–N, nitrate-N, total nitrogen, dissolved reactive phosphorus, total phosphorus, and chlorophyll-a (Chlo-a). Water temperature was determined by a mercury thermometer. The concentration of hydrogen ion (pH) was determined by pH meter Model 59003-20 USA.
Recommended publications
  • Trophic Transfer of Mercury in a Subtropical Coral Reef Food Web
    Trophic Transfer of Mercury in a Subtropical Coral Reef Food Web _______________________________________________________________________ A Thesis Presented to The Faculty of the College of Arts and Sciences Florida Gulf Coast University In Partial Fulfillment Of the Requirement for the Degree of Master of Science ________________________________________________________________________ By Christopher Tyler Lienhardt 2015 APPROVAL SHEET This thesis is submitted in partial fulfillment of the requirements for the degree of Master of Science ____________________________ Christopher Tyler Lienhardt Approved: July 2015 ____________________________ Darren G. Rumbold, Ph.D. Committee Chair / Advisor ____________________________ Michael L. Parsons, Ph.D. ____________________________ Ai Ning Loh, Ph. D. The final copy of this thesis has been examined by the signatories, and we find that both the content and the form meet acceptable presentation standards of scholarly work in the above mentioned discipline. i Acknowledgments This research would not have been possible without the support and encouragement of numerous friends and family. First and foremost I would like to thank my major advisor, Dr. Darren Rumbold, for giving me the opportunity to play a part in some of the great research he is conducting, and add another piece to the puzzle that is mercury biomagnification research. The knowledge, wisdom and skills imparted unto me over the past three years, I cannot thank him enough for. I would also like to thank Dr. Michael Parsons for giving me a shot to be a part of the field team and assist in the conducting of our research. I also owe him thanks for his guidance and the nature of his graduate courses, which helped prepare me to take on such a task.
    [Show full text]
  • A New Type of Plankton Food Web Functioning in Coastal Waters Revealed by Coupling Monte Carlo Markov Chain Linear Inverse Metho
    A new type of plankton food web functioning in coastal waters revealed by coupling Monte Carlo Markov Chain Linear Inverse method and Ecological Network Analysis Marouan Meddeb, Nathalie Niquil, Boutheina Grami, Kaouther Mejri, Matilda Haraldsson, Aurélie Chaalali, Olivier Pringault, Asma Sakka Hlaili To cite this version: Marouan Meddeb, Nathalie Niquil, Boutheina Grami, Kaouther Mejri, Matilda Haraldsson, et al.. A new type of plankton food web functioning in coastal waters revealed by coupling Monte Carlo Markov Chain Linear Inverse method and Ecological Network Analysis. Ecological Indicators, Elsevier, 2019, 104, pp.67-85. 10.1016/j.ecolind.2019.04.077. hal-02146355 HAL Id: hal-02146355 https://hal.archives-ouvertes.fr/hal-02146355 Submitted on 3 Jun 2019 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. 1 A new type of plankton food web functioning in coastal waters revealed by coupling 2 Monte Carlo Markov Chain Linear Inverse method and Ecological Network Analysis 3 4 5 Marouan Meddeba,b*, Nathalie Niquilc, Boutheïna Gramia,d, Kaouther Mejria,b, Matilda 6 Haraldssonc, Aurélie Chaalalic,e,f, Olivier Pringaultg, Asma Sakka Hlailia,b 7 8 aUniversité de Carthage, Faculté des Sciences de Bizerte, Laboratoire de phytoplanctonologie 9 7021 Zarzouna, Bizerte, Tunisie.
    [Show full text]
  • Crustacean Zooplankton in Lake Constance from 1920 to 1995: Response to Eutrophication and Re-Oligotrophication
    Arch. Hydrobiol. Spec. Issues Advanc. Limnol. 53, p. 255-274, December 1998 Lake Constance, Characterization of an ecosystem in transition Crustacean zooplankton in Lake Constance from 1920 to 1995: Response to eutrophication and re-oligotrophication Dietmar Straile and Waiter Geller with 9 figures Abstract: During the first three quarters ofthis century, the trophic state ofLake Constance changed from oligotrophic to meso-/eutrophic conditions. The response ofcrustaceans to the eutrophication process is studied by comparing biomasses ofcrustacean zooplankton from recent years, i.e. from 1979-1995, with data from the early 1920s (AUERBACH et a1. 1924, 1926) and the 1950s (MUCKLE & MUCKLE­ ROTTENGATTER 1976). This comparison revealed a several-fold increase in crustacean biomass. The relative biomass increase was more pronounced from the early 1920s to the 1950s than from the 1950s to the 1980s. Most important changes ofthe species inventory included the invasion of Cyclops vicinus and Daphnia galeata and the extinction of Heterocope borealis and Diaphanosoma brachyurum during the 1950s and early 1960s. All species which did not become extinct increased their biomass during eutrophication. This increase in biomass differed between species and throughout the season which re­ sulted in changes in relative biomass between species. Daphnids were able to enlarge their seasonal window ofrelative dominance from 3 months during the 1920s (June to August) to 7 months during the 1980s (May to November). On an annual average, this resulted in a shift from a copepod dominated lake (biomass ratio cladocerans/copepods = 0.4 during 1920/24) to a cladoceran dominated lake (biomass ratio cladocerans/copepods = 1.5 during 1979/95).
    [Show full text]
  • Biomagnification of Methylmercury in a Marine Plankton Ecosystem
    EGU2020-1695, updated on 01 Oct 2021 https://doi.org/10.5194/egusphere-egu2020-1695 EGU General Assembly 2020 © Author(s) 2021. This work is distributed under the Creative Commons Attribution 4.0 License. Biomagnification of methylmercury in a marine plankton ecosystem Peipei Wu1, Emily Zakem2,3, Stephanie Dutkiewicz2, and Yanxu Zhang1 1School of Atmospheric Sciences, Nanjing University, Nanjing, Jiangsu, China ([email protected]) 2Department of Earth, Atmospheric, and Planetary Sciences, Massachusetts Institute of Technology, USA 3Department of Biological Sciences, University of Southern California, Los Angeles,USA Methylmercury is greatly bioconcentrated and biomagnified in marine plankton ecosystems, and these communities form the basis of marine food webs. Therefore, evaluating the potential exposure of methylmercury to higher trophic levels, including humans, requires a better understanding of its distribution in the ocean and the factors that control its biomagnification. In this study, a coupled physical/ecological model was used to simulate the trophic transfer of monomethylmercury (MMHg) in a marine plankton ecosystem. The model includes phytoplankton, a microbial community, herbivorous zooplankton (HZ), and carnivorous zooplankton (CZ). The model captured both shorter food chains in oligotrophic regions, with small HZ feeding on small phytoplankton, and longer chains in higher nutrient conditions, with larger HZ feeding on larger phytoplankton and larger CZ feeding on larger HZ. In the model, trophic dilution occurred in the food webs that involved small zooplankton, as the grazing fluxes of small zooplankton were insufficient to accumulate more MMHg in themselves than in their prey. The model suggested that biomagnification was more prominent in large zooplankton and that the microbial community played an important role in the trophic transfer of MMHg.
    [Show full text]
  • Efficiency of the Using of Human and Machine the Sources in Wheat Production in Beheira Governorate
    Available online at http://www.journalijdr.com International Journal of Development Research ISSN: 2230-9926 Vol. 11, Issue, 07, pp. 48934-48940, July, 2021 https://doi.org/10.37118/ijdr.22437.07.2021 RESEARCH ARTICLE OPEN ACCESS EFFICIENCY OF THE USING OF HUMAN AND MACHINE THE SOURCES IN WHEAT PRODUCTION IN BEHEIRA GOVERNORATE Ashraf M. El Dalee1,*, Lamis F. Elbahenasy2, Safaa M. Elwakeel2 and Eman A. Ibrahim3 1Professor Researcher, Agricultural Economics Research Institute, Agricultural Research Center –Egypt 2Senior Researcher, Agricultural Economics Research Institute Agricultural Research Center – Egypt 3Researcher, Agricultural Economics Research Institute, Agricultural Research Center – Egypt ARTICLE INFO ABSTRACT The research problem is represented in the high costs of producing wheat crop as a result of the high prices of Article History: production requirements, which may affect the cultivated areas of it, and due to the rapid and successive Received 20th April, 2021 progress in the transfer of technology in the field of agriculture, especially agricultural operations, it has been Received in revised form possible to replace human work with automated work, after the high wages of rural labor trained women in the 10th May, 2021 fields of agriculture and continuous migration to urban areas as a result of the seasonality of agricultural Accepted 30th June, 2021 production on the one hand, and the low wages in the country side compared to the urban ones, which Published online 28th July, 2021 prompted farmers to move towards using
    [Show full text]
  • Enhancing Climate Change Adaptation in the North Coast and Nile Delta Regions in Egypt Environmental and Social Management Frame
    Annex VI (b) – Environmental and Social Management Framework Green Climate Fund Funding Proposal I Enhancing Climate Change Adaptation in the North Coast and Nile Delta Regions in Egypt Environmental and Social Management Framework 31 August 2017 FP-UNDP-050617-5945- Annex VI (b) 17 Aug 2017.docx 1 Annex VI (b) – Environmental and Social Management Framework Green Climate Fund Funding Proposal I CONTENTS Contents ................................................................................................................................................. 2 Executive Summary ............................................................................................................................... 8 1 Introduction ................................................................................................................................ 10 1.1 Background ................................................................................................................................. 10 1.2 Overview of the Project ............................................................................................................... 11 1.2.1 Summary of Activities .......................................................................................................... 12 1.2.2 Construction Material .......................................................................................................... 17 1.3 Environmental and Social Risk Assessment ............................................................................... 18 1.3.1
    [Show full text]
  • Ecology (Pyramids, Biomagnification, & Succession
    ENERGY PYRAMIDS & Freshmen Biology FOOD CHAINS/FOOD WEBS May 4 – May 8 Lecture ENERGY FLOW •Energy → powers life’s processes •Energy = ATP! •Flow of energy determines the system’s ability to sustain life FEEDING RELATIONSHIPS • Energy flows through an ecosystem in one direction • Sun → autotrophs (producers) → heterotrophs (consumers) FOOD CHAIN VS. FOOD WEB FOOD CHAINS • Energy stored by producers → passed through an ecosystem by a food chain • Food chain = series of steps in which organisms transfer energy by eating and being eaten FOOD WEBS •Feeding relationships are more complex than can be shown in a food chain •Food Web = network of complex interactions •Food webs link all the food chains in an ecosystem together ECOLOGICAL PYRAMIDS • Used to show the relationships in Ecosystems • There are different types: • Energy Pyramid • Biomass Pyramid • Pyramid of numbers ENERGY PYRAMID • Only part of the energy that is stored in one trophic level can be passed on to the next level • Much of the energy that is consumed is used for the basic functions of life (breathing, moving, reproducing) • Only 10% is used to produce more biomass (10 % moves on) • This is what can be obtained from the next trophic level • All of the other energy is lost 10% RULE • Only 10% of energy (from organisms) at one trophic level → the next level • EX: only 10% of energy/calories from grasses is available to cows • WHY? • Energy used for bodily processes (growth/development and repair) • Energy given off as heat • Energy used for daily functioning/movement • Only 10% of energy you take in should be going to your actual biomass/weight which another organism could eat BIOMASS PYRAMID • Total amount of living tissue within a given trophic level = biomass • Represents the amount of potential food available for each trophic level in an ecosystem PYRAMID OF NUMBERS •Based on the number of individuals at each trophic level.
    [Show full text]
  • Toxic Chemical Contaminants
    4 NaturalNatural RegionsRegions ofof thethe GulfGulf ofof MaineMaine TOXIC CHEMICAL CONTAMINANTS STATE OF THE GULF OF MAINE REPORT Gulf of Maine Census Marine Life May 2013 TOXIC CHEMICAL CONTAMINANTS STATE OF THE GULF OF MAINE REPORT TABLE OF CONTENTS 1. Issue in Brief ................................................................................................... 1 2. Driving Forces and Pressures .......................................................................4 2.1 Human .................................................................................................4 2.2 Natural .................................................................................................6 3. Status and Trends ..........................................................................................7 4. Impacts ........................................................................................................ 15 4.1 Biodiversity and Ecosystem Impacts ................................................ 15 4.2 Human Health ....................................................................................17 4.3 Economic Impacts ............................................................................. 18 5. Actions and Responses ............................................................................... 19 5.1 Legislation and Policy........................................................................ 19 5.2 Contaminant Monitoring ...................................................................20 6. Indicator Summary ......................................................................................23
    [Show full text]
  • Fertilizing the Ocean with Iron Is This a Viable Way to Help Reduce Carbon Dioxide Levels in the Atmosphere?
    380 Fertilizing the Ocean with Iron Is this a viable way to help reduce carbon dioxide levels in the atmosphere? 360 ive me half a tanker of iron, and I’ll give you an ice Twenty years on, Martin’s line is still viewed alternately age” may rank as the catchiest line ever uttered by a as a boast or a quip—an opportunity too good to pass up or a biogeochemist.“G The man responsible was the late John Martin, misguided remedy doomed to backfire. Yet over the same pe- former director of the Moss Landing Marine Laboratory, who riod, unrelenting increases in carbon emissions and mount- discovered that sprinkling iron dust in the right ocean waters ing evidence of climate change have taken the debate beyond could trigger plankton blooms the size of a small city. In turn, academic circles and into the free market. the billions of cells produced might absorb enough heat-trap- Today, policymakers, investors, economists, environ- ping carbon dioxide to cool the Earth’s warming atmosphere. mentalists, and lawyers are taking notice of the idea. A few Never mind that Martin companies are planning new, was only half serious when larger experiments. The ab- 340 he made the remark (in his Ocean Iron Fertilization sence of clear regulations for “best Dr. Strangelove accent,” either conducting experiments he later recalled) at an infor- An argument for: Faced with the huge at sea or trading the results mal seminar at Woods Hole consequences of climate change, iron’s in “carbon offset” markets Oceanographic Institution outsized ability to put carbon into the oceans complicates the picture.
    [Show full text]
  • Biological Oceanography - Legendre, Louis and Rassoulzadegan, Fereidoun
    OCEANOGRAPHY – Vol.II - Biological Oceanography - Legendre, Louis and Rassoulzadegan, Fereidoun BIOLOGICAL OCEANOGRAPHY Legendre, Louis and Rassoulzadegan, Fereidoun Laboratoire d'Océanographie de Villefranche, France. Keywords: Algae, allochthonous nutrient, aphotic zone, autochthonous nutrient, Auxotrophs, bacteria, bacterioplankton, benthos, carbon dioxide, carnivory, chelator, chemoautotrophs, ciliates, coastal eutrophication, coccolithophores, convection, crustaceans, cyanobacteria, detritus, diatoms, dinoflagellates, disphotic zone, dissolved organic carbon (DOC), dissolved organic matter (DOM), ecosystem, eukaryotes, euphotic zone, eutrophic, excretion, exoenzymes, exudation, fecal pellet, femtoplankton, fish, fish lavae, flagellates, food web, foraminifers, fungi, harmful algal blooms (HABs), herbivorous food web, herbivory, heterotrophs, holoplankton, ichthyoplankton, irradiance, labile, large planktonic microphages, lysis, macroplankton, marine snow, megaplankton, meroplankton, mesoplankton, metazoan, metazooplankton, microbial food web, microbial loop, microheterotrophs, microplankton, mixotrophs, mollusks, multivorous food web, mutualism, mycoplankton, nanoplankton, nekton, net community production (NCP), neuston, new production, nutrient limitation, nutrient (macro-, micro-, inorganic, organic), oligotrophic, omnivory, osmotrophs, particulate organic carbon (POC), particulate organic matter (POM), pelagic, phagocytosis, phagotrophs, photoautotorphs, photosynthesis, phytoplankton, phytoplankton bloom, picoplankton, plankton,
    [Show full text]
  • Mercury and Methyl Mercury in Sediments of Northern Lakes-Egypt
    Journal of Environmental Protection, 2012, 3, 254-261 http://dx.doi.org/10.4236/jep.2012.33032 Published Online March 2012 (http://www.SciRP.org/journal/jep) Mercury and Methyl Mercury in Sediments of Northern Lakes-Egypt Mohamed A. Shreadah1, Safaa A. Abdel Ghani1, Asia Abd El Samie Taha2, Abd El Moniem M. Ahmed2, Hamada B. I. Hawash1 1National Institute of Oceanography and Fisheries, Alexandria, Egypt; 2Chemistry Department, Faculty of Science, Alexandria Uni- versity, Alexandria, Egypt. Email: [email protected] Received December 1st, 2011; revised January 16th, 2012; accepted February 18th, 2012 ABSTRACT Fifty-four sediment samples of the five Northern Egyptian lakes, (Mariout, Edku, El-Burullus, El-Manzallah, and El- Bardaweel) were analyzed to investigate the pollution status of mercury (Hg). The total mercury (T-Hg) content in sediment samples ranged from 15.33 to 171.29 ng·g–1 dry wt). The results showed that T-Hg were lower than the back ground values reported and also lower than the ranges of uncontaminated sediments. Moreover, the T-Hg concentra- tions in all sediments were under the upper chemical Exceedance level (1 µg·g–1). The concentrations of Methyl mer- cury (MeHg) in surface sediments of the Northern lakes ranged from 0.002 - 0.023 ng·g–1 dry wt. The contribution of MeHg was less than 0.1% of total mercury concentration with index values from 0.08 - 1.37 ng·g–1; dry wt). MeHg showed insignificant correlation with T-Hg. This suggested that MeHg contents were not controlled by the T-Hg in sediments. The T-Hg and MeHg concentrations were insignificantly correlated with TOC content which indicates that the concentration of T-Hg and MeHg in sediments of Northern lakes were not influence by TOC.
    [Show full text]
  • SSWIMS: Plankton
    Unit Six SSWIMS/Plankton Unit VI Science Standards with Integrative Marine Science-SSWIMS On the cutting edge… This program is brought to you by SSWIMS, a thematic, interdisciplinary teacher training program based on the California State Science Content Standards. SSWIMS is provided by the University of California Los Angeles in collaboration with the Los Angeles County school districts, including the Los Angeles Unified School District. SSWIMS is funded by a major grant from the National Science Foundation. Plankton Lesson Objectives: Students will be able to do the following: • Determine a basis for plankton classification • Differentiate between various plankton groups • Compare and contrast plankton adaptations for buoyancy Key concepts: phytoplankton, zooplankton, density, diatoms, dinoflagellates, holoplankton, meroplankton Plankton Introduction “Plankton” is from a Greek word for food chains. They are autotrophs, “wanderer.” It is a making their own food, using the collective term for process of photosynthesis. The the various animal plankton or zooplankton eat organisms that drift or food for energy. These swim weakly in the heterotrophs feed on the open water of the sea or microscopic freshwater lakes and ponds. These world of the weak swimmers, carried about by sea and currents, range in size from the transfer tiniest microscopic organisms to energy up much larger animals such as the food jellyfish. pyramid to fishes, marine mammals, and humans. Plankton can be divided into two large groups: planktonic plants and Scientists are interested in studying planktonic animals. The plant plankton, because they are the basis plankton or phytoplankton are the for food webs in both marine and producers of ocean and freshwater freshwater ecosystems.
    [Show full text]